JP2000024679A - Treating device of high concentration sewage - Google Patents

Treating device of high concentration sewage

Info

Publication number
JP2000024679A
JP2000024679A JP10197892A JP19789298A JP2000024679A JP 2000024679 A JP2000024679 A JP 2000024679A JP 10197892 A JP10197892 A JP 10197892A JP 19789298 A JP19789298 A JP 19789298A JP 2000024679 A JP2000024679 A JP 2000024679A
Authority
JP
Japan
Prior art keywords
filter medium
tank
nitrification
nitrification tank
water
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10197892A
Other languages
Japanese (ja)
Inventor
Susumu Mori
享 森
Shigeyuki Fujimura
重幸 藤村
Osamu Yamashita
修 山下
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Ishigaki Co Ltd
Original Assignee
Ishigaki Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Ishigaki Co Ltd filed Critical Ishigaki Co Ltd
Priority to JP10197892A priority Critical patent/JP2000024679A/en
Publication of JP2000024679A publication Critical patent/JP2000024679A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

PROBLEM TO BE SOLVED: To obtain a treating device of a high concn. sewage capable of removing nitrogen and SS in raw water and moreover, easy in regeneration by washing of a filter medium. SOLUTION: In a circulation type nitrification/denitrification device in which a denitrification tank 1 and a nitrification tank 2 are arranged side by side, treated water in the denitrification tank 1 is supplied to the nitrification tank 2 and a part of the treated water in the nitrification tank 2 is returned to the denitrification tank 1, a filter medium layer is formed in the tank by using a floatable filter medium piece made of a synthetic resin-made fiber as a filter medium 3 to be packed in the nitrification tank 2 and an air diffusing pipe 8a for washing is disposed under the filter medium layer. The filter medium 3 is large in a contact area with the sewage, high in strength and good in water permeability, suitable for the sewage treatment and also easy in regeneration by washing.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】この発明は、下水等の有機性
汚水の処理装置に関する。
The present invention relates to an apparatus for treating organic sewage such as sewage.

【0002】[0002]

【従来の技術】従来、有機性汚水の処理装置は公知であ
る。比重が1.0以上のアンスラサイト、セラミック等
のろ材を用いた硝化装置はよく知られている。また、比
重が1に近い浮上性のろ材を用いた硝化装置は多数あ
り、これらの装置に用いられているろ材の形状および寸
法は、直方体で10〜30mmの正方形に5〜25mm
の厚さをもったもの等が知られている。これらのろ材寸
法は、アンスラサイトやセラミック等のろ材に比べ大き
い。これは、ろ層の目詰まり防止のためと考えられる
が、ろ材寸法が大きすぎると、ろ過抵抗が均一ではな
く、抵抗の低い部分に被処理水が多く流れる、いわゆる
偏流現象が生じ、処理に支障を来たす結果となる。さら
に、合成繊維を束ねたり、繭状に成形した繊維ろ材と称
するろ材も多数ある。これらは、一種類の繊維からでき
たものが多く、ろ過抵抗が上昇したり、水抜き時に重力
により強く押し付けられ、変形することがある。また、
上向流式ろ過は、原水と空気が同一方向に流れるのでS
Sが処理水にもれやすい欠点がある。
2. Description of the Related Art Conventionally, apparatuses for treating organic wastewater are known. A nitrification apparatus using a filter medium such as anthracite or ceramic having a specific gravity of 1.0 or more is well known. In addition, there are many nitrification apparatuses using a buoyant filter medium having a specific gravity close to 1, and the shape and dimensions of the filter medium used in these apparatuses are 5 to 25 mm in a rectangular parallelepiped 10 to 30 mm square.
Are known. These filter media dimensions are larger than filter media such as anthracite and ceramic. This is considered to prevent clogging of the filter layer.However, if the filter medium size is too large, the filtration resistance is not uniform, and a large amount of water to be treated flows into a low resistance portion, so-called a drift phenomenon, and the treatment is difficult. This results in trouble. Furthermore, there are many filter media called fiber filter media in which synthetic fibers are bundled or formed into a cocoon shape. Many of these are made of one type of fiber, which may increase the filtration resistance or may be deformed by being strongly pressed by gravity during drainage. Also,
In the upward flow filtration, raw water and air flow in the same direction,
There is a disadvantage that S easily leaks into the treated water.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、比重が
1に近い浮上性のろ材を用いた高負荷処理装置では、ろ
過速度が小さいため、ろ材の圧密度が十分でなく、層内
を上昇する空気と共にSSが処理水に抜け出ることがあ
る。また比重の大きいアンスラサイトやセラミックろ
材、あるいは比重が極端に小さい発泡性のろ材等では、
空隙率が小さくSSによる目詰まりが短時間で生じ、洗
浄頻度が高くなるし、洗浄に大きな動力を必要とする。
そして、この硝化槽の煩雑な洗浄は、増殖速度の遅い硝
化菌を流出してしまうことになる。さらに、寸法の大き
いろ材では偏流現象が生じ、処理に支障を来たす。
However, in a high-load processing apparatus using a buoyant filter medium having a specific gravity close to 1, the filtering speed is low, so that the pressure density of the filter medium is not sufficient, and air rising in the layer is not sufficient. At the same time, SS may escape into the treated water. In the case of anthracite or ceramic filter media with a large specific gravity, or foamable filter media with an extremely small specific gravity,
Porosity is small, clogging by SS occurs in a short time, cleaning frequency increases, and large power is required for cleaning.
Then, the complicated washing of the nitrification tank causes nitrifying bacteria having a low growth rate to flow out. Furthermore, a large-sized filter medium causes a drift phenomenon, which hinders processing.

【0004】[0004]

【課題を解決するための手段】この発明は、硝化槽に装
入するろ材に工夫をするとともに、ろ材層高と水層高と
の比率を適切にすること、およびろ過水の一部を循環す
ることによって微細なSSまでも捕捉しながら、目詰ま
りし難くかつ逆洗が容易なろ材層を形成したものであ
る。すなわち、ろ材として素材が芯をポリプロピレン、
鞘をポリエチレンとした熱融着性複合繊維で繊度が18
〜65デニールである第1フィラメントと、素材がポリ
プロピレン繊維で繊度が3〜10デニールである第2フ
ィラメントと、素材が芯をポリプロピレン、鞘をポリエ
チレンとした熱融着性複合繊維で繊度が1.5〜6デニ
ールである第3フィラメントを混綿したウェッブをニー
ドルパンチング法により布形化し、両面のウェッブ起毛
状態を平滑化することなく加熱処理し、前記ウェッブの
重量が200〜800g/平方メートル、厚みが2〜8
mmの布形化板状体を製作し、この布形化板状体を3〜
5mm角に裁断したものをろ材として用いたものであ
る。また、ろ材層高と水層高との比率を65:35〜5
0:50とすることで、ろ材の洗浄を容易にし、さら
に、ろ材の圧密不足によって空気と共にSSが処理水に
抜け出る欠点を、処理水を循環することで圧密度を高く
して解決したものである。
According to the present invention, a filter medium to be charged into a nitrification tank is devised, an appropriate ratio between a filter medium layer height and a water layer height is provided, and a part of filtered water is circulated. By doing so, a filter medium layer is formed that is hardly clogged and easy to backwash while capturing even fine SS. That is, the core material is polypropylene as the filter medium,
A heat-fusible conjugate fiber made of polyethylene and having a fineness of 18
A first filament having a denier of 65 to 65 denier; a second filament having a denier of 3 to 10 denier made of polypropylene fiber; and a heat-fusible composite fiber having a core of polypropylene and a sheath of polyethylene having a denier of 1. A web mixed with a third filament having a denier of 5 to 6 is formed into a cloth by a needle punching method, and is heated without smoothing the state of raising the web on both sides. 2-8
mm of a cloth-shaped plate, and the cloth-shaped plate is 3 to 3 mm.
The material cut into 5 mm squares was used as a filter medium. Further, the ratio between the height of the filter medium layer and the height of the water layer is set to 65:35 to 5
By setting the ratio to 0:50, washing of the filter medium is facilitated, and furthermore, the disadvantage that the SS escapes into the treated water together with air due to insufficient consolidation of the filter medium is solved by increasing the pressure density by circulating the treated water. is there.

【0005】[0005]

【発明の実施の形態】上記布形化板状体ろ材は、不織布
であるため空隙率が大きく、微生物の付着に優れてい
る。このため、ろ層中の微生物量を大きく保つことがで
きる。また、ろ過圧力や水抜き時の重力による押しつぶ
れを防止するため、太さの異なる3種類のフィラメント
を用いている。上記布形化板状体ろ材は、密に詰まって
いるのに空隙率が大きいので、目詰まりによる圧力損失
は小さく、ろ過時間が長い。洗浄は、ろ材層高:水層高
の比を65:35〜50:50とすることで、下方から
の散気で容易に流動し、捕捉されたSSや余剰汚泥を分
離することができる。この時の空気量はアンスラサイト
やセラミックろ材の装置に比べ少なくてすむ。また、上
向流式の欠点であるSS漏れについて、処理水を循環す
ることで解決し、従来より低いSSの処理水が得られ
る。さらに循環することにより酸素を十分に溶解した処
理水を原水に混合するため、曝気空気量が従来装置より
少なくてよい。以下この発明に係るろ材を用いた汚水処
理装置を図面に基づいて説明する。
BEST MODE FOR CARRYING OUT THE INVENTION The above-mentioned cloth-shaped plate-shaped filter medium is a non-woven fabric, so that it has a high porosity and is excellent in adhering microorganisms. Therefore, the amount of microorganisms in the filter layer can be kept large. In addition, three types of filaments having different thicknesses are used in order to prevent crushing due to gravity at the time of filtration pressure or drainage. The cloth-shaped plate-shaped filter medium is densely packed but has a high porosity, so that pressure loss due to clogging is small and filtration time is long. In the washing, by setting the ratio of the filter medium layer height to the water layer height to 65:35 to 50:50, it is easy to flow by diffused air from below, and the trapped SS and excess sludge can be separated. At this time, the amount of air is smaller than that of an anthracite or ceramic filter medium device. Further, the SS leakage, which is a drawback of the upward flow type, is solved by circulating the treated water, and the treated water having a lower SS than before can be obtained. Further, since the circulated water mixes the treated water in which oxygen is sufficiently dissolved into the raw water, the amount of aerated air may be smaller than that of the conventional apparatus. Hereinafter, a sewage treatment apparatus using a filter medium according to the present invention will be described with reference to the drawings.

【0006】[0006]

【実施例】図1は、この発明に係る処理装置を示し、図
に随って説明する。図1において、符号1はその下部を
逆円錐状に形成して沈殿部を設けた脱窒槽、2は同じく
下部を逆円錐状に形成して沈殿部を設けた硝化槽、3は
脱窒槽および硝化槽に装入したろ材、4は原水の供給管
であり、5は処理水の取り出し管、6は硝化処理水の一
部を脱窒槽に循環する循環経路、6aは循環用のポン
プ、7は脱窒処理水を硝化槽2に供給する管、8は洗浄
用空気の供給管、8aは洗浄用散気管、8bは曝気用散
気管、9は硝化処理水の一部を循環する硝化循環経路、
9aは循環ポンプである。
FIG. 1 shows a processing apparatus according to the present invention, which will be described with reference to the drawings. In FIG. 1, reference numeral 1 denotes a denitrification tank in which the lower part is formed in an inverted cone shape and a settling portion is provided, 2 denotes a nitrification tank in which the lower portion is formed in an inverted cone shape and a settlement portion is provided, 3 denotes a denitrification tank and A filter medium charged in the nitrification tank, 4 is a supply pipe for raw water, 5 is a pipe for taking out treated water, 6 is a circulation path for circulating a part of the nitrification treated water to the denitrification tank, 6a is a pump for circulation, 7 Is a pipe for supplying denitrification water to the nitrification tank 2, 8 is a supply pipe for cleaning air, 8a is a diffuser pipe for cleaning, 8b is a diffuser pipe for aeration, and 9 is a nitrification circulator for circulating a part of the nitrification water. Route,
9a is a circulation pump.

【0007】この発明に係る装置は、上述のように構成
してあるので、原水は硝化槽2からの硝化処理水と混合
されて、脱窒槽1に供給される。脱窒槽1に供給された
混合水は、ろ材層中を上昇して微細なSSが捕捉除去さ
れると同時に、ろ材3に生息する嫌気性微生物に触れる
ことによって、硝化液を脱窒したり、有機性汚濁物が嫌
気的に分解されて、脱窒槽1の上部を通り硝化槽2に供
給される。硝化槽2では、ろ材層中を上昇して原水中の
主にアンモニア性窒素が、硝化菌の働きによって硝酸と
なり、一部は処理水として取り出し、残りは原水と混合
されて、脱窒槽1に循環供給され、また、一部は硝化槽
入口へ循環供給される。
[0007] Since the apparatus according to the present invention is configured as described above, raw water is mixed with the nitrification-treated water from the nitrification tank 2 and supplied to the denitrification tank 1. The mixed water supplied to the denitrification tank 1 rises in the filter medium layer to capture and remove fine SS, and at the same time, touches the anaerobic microorganisms inhabiting the filter medium 3 to denitrify the nitrification liquid, Organic pollutants are anaerobically decomposed and supplied to the nitrification tank 2 through the upper part of the denitrification tank 1. In the nitrification tank 2, ascending in the filter medium layer, mainly ammoniacal nitrogen in the raw water becomes nitric acid by the action of nitrifying bacteria, a part of which is taken out as treated water, and the rest is mixed with the raw water to be denitrified in the denitrification tank 1. It is circulated and partly circulated to the nitrification tank inlet.

【0008】このような処理運転時に、この発明に係る
ろ材3は、合成樹脂製の繊維ろ材であるので接触面積が
広く、汚水中の汚濁物を効率よく分解することができる
とともに、強度を有するので、原水圧によってその目が
押しつぶされることがなく、目詰りしにくく長時間の運
転が可能である。
[0008] During such a treatment operation, the filter medium 3 according to the present invention is a synthetic resin fiber filter medium, so that it has a large contact area, can efficiently decompose pollutants in wastewater, and has strength. Therefore, the eyes are not crushed by the raw water pressure, and the eyes are hardly clogged, and long-time operation is possible.

【0009】次に、このような運転をして、ろ材層がS
Sおよび有機物質の分解時や、脱窒あるいは硝化時に生
じた汚泥等で目詰まりしたときは、各々供給液を停止し
て、各々個別に洗浄を行う。すなわち、供給管8からの
空気でろ材層をときほぐし攪拌し、同時に洗浄水を送っ
て、ろ材3から分離したSSを槽外に排出する。そし
て、排出が完了したのち、原水を供給して運転を再開す
る。このろ材3の洗浄操作においても、この発明のろ材
3は、合成樹脂製の繊維ろ材であるので、通水性が良好
でほぐし易く、強度を有するので、撹拌による損耗もな
いものである。
Next, by performing such an operation, the filter medium layer becomes S
When clogging is caused by sludge or the like generated during decomposition of S and organic substances or during denitrification or nitrification, the supply liquids are stopped, and washing is performed individually. That is, the filter medium layer is loosened and stirred with the air from the supply pipe 8, and at the same time, the washing water is sent to discharge the SS separated from the filter medium 3 out of the tank. Then, after the discharge is completed, raw water is supplied to restart the operation. Also in the washing operation of the filter medium 3, since the filter medium 3 of the present invention is a synthetic resin fiber filter medium, it has good water permeability, is easy to loosen, and has strength, so that it is not worn by stirring.

【0010】また、上記ろ材3を撹拌するに当って、処
理槽1、2の中心部に立設したドラフトチューブ1a、
2aは、その下部開口に設けた洗浄用散気管8aからの
空気を案内して槽内に洗浄水の上下循環流を形成して効
率よくろ材3を撹拌洗浄することができるものである。
また、ろ材層高と水層高の比率を65:35〜50:5
0としたのは、この比率が上述のろ材撹拌洗浄時におい
て、ろ材3を最も効率的に撹拌流動させるろ材量と水量
の割合を見出したことによるものである。
Further, in stirring the filter medium 3, a draft tube 1a, which is provided upright at the center of the processing tanks 1, 2,
Numeral 2a guides the air from the cleaning air diffuser 8a provided in the lower opening to form a vertical circulating flow of the cleaning water in the tank so that the filter medium 3 can be efficiently stirred and cleaned.
Further, the ratio of the height of the filter medium layer to the height of the water layer is set to 65:35 to 50: 5.
The reason why the ratio is set to 0 is that the ratio has found the ratio between the amount of the filter medium and the amount of water that allows the filter medium 3 to be stirred and flow most efficiently during the above-described filter medium stirring and washing.

【0011】[0011]

【発明の効果】以上のように、この発明では合成樹脂繊
維材で構成したろ材を用いた汚水の硝化装置において、
処理水部と流入部を循環ポンプを介して接続し、処理水
の一部を循環すること、およびろ材層高と水層高との比
率を撹拌に適切となるように装入することにより微細な
SSや有機性汚濁物質を単一槽で分離除去ができ、特に
循環によりろ層形成が安定化し、処理水の溶存酸素が再
利用できて汚水の高度な硝化が可能となり、また、ブロ
ワ動力の節減が可能となるとともに、完全なろ材の洗浄
を可能にしたものである。
As described above, according to the present invention, in a sewage nitrifying apparatus using a filter medium made of synthetic resin fiber material,
The treated water section and the inflow section are connected via a circulation pump to circulate part of the treated water, and the ratio between the height of the filter medium layer and the height of the water layer is charged so as to be appropriate for stirring. SS and organic pollutants can be separated and removed in a single tank. In particular, the formation of the filter layer is stabilized by circulation, the dissolved oxygen in the treated water can be reused, and the advanced nitrification of the wastewater becomes possible. This makes it possible to reduce the amount of waste and to completely wash the filter medium.

【図面の簡単な説明】[Brief description of the drawings]

【図1】この発明に係る高濃度汚水の処理装置の系統図
である。
FIG. 1 is a system diagram of a high-concentration sewage treatment apparatus according to the present invention.

【図2】この発明に係る高濃度汚水の処理装置に用いる
ろ材の斜面図である。
FIG. 2 is a perspective view of a filter medium used in the high-concentration sewage treatment apparatus according to the present invention.

【符号の説明】[Explanation of symbols]

1 脱窒槽 2 硝化槽 3 ろ材 8a 洗浄用散気管 9a 循環ポンプ DESCRIPTION OF SYMBOLS 1 Denitrification tank 2 Nitrification tank 3 Filter medium 8a Cleaning diffuser 9a Circulation pump

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 脱窒槽1と硝化槽2を並列し、脱窒槽1
の処理水を硝化槽2に供給し、硝化槽2の処理水の一部
を脱窒槽1に返送するようにした循環式硝化脱窒装置に
おいて、硝化槽2に装入するろ材3を合成樹脂製の繊維
材よりなる浮上性のろ材片として槽内にろ過層を形成
し、このろ過層の下方に洗浄用散気管8aを配設してな
る高濃度汚水の処理装置。
1. A denitrification tank 1 and a nitrification tank 2 are arranged in parallel.
Is supplied to the nitrification tank 2 and a filter medium 3 charged into the nitrification tank 2 is made of synthetic resin in a circulating nitrification denitrification apparatus in which the treated water of the nitrification tank 2 is returned to the denitrification tank 1. An apparatus for treating high-concentration sewage, in which a filtration layer is formed in a tank as a buoyant filter medium piece made of a fiber material made of stainless steel, and a diffuser 8a for washing is disposed below the filtration layer.
【請求項2】 上記硝化槽2に装入するろ材3の素材が
芯をポリプロピレン、鞘をポリエチレンとした熱融着性
複合繊維で繊度が18〜65デニールである第1フィラ
メントと、素材がポリプロピレン繊維で繊度が3〜10
デニールである第2フィラメントと、素材が芯をポリプ
ロピレン、鞘をポリエチレンとした熱融着性複合繊維で
繊度が1.5〜6デニールである第3フィラメントを混
綿したウェッブをニードルパンチング法により布形化
し、両面のウェッブ起毛状態を平滑化することなく加熱
処理し、前記ウェッブの重量が200〜800g/平方
メートル、厚みが2〜8mmの布形化板状体を製作し、
この布形化板状体を3〜5mm角に裁断したものをろ材
として装入している請求項1記載の高濃度汚水の処理装
置。
2. A first filament having a denier of 18 to 65 denier, a heat-fusible conjugate fiber having a core of polypropylene and a sheath of polyethylene, and a material of polypropylene, wherein the material of the filter medium 3 charged into the nitrification tank 2 is polypropylene. Fiber with fineness of 3-10
A web formed by mixing a denier second filament and a heat-fusible conjugate fiber having a core of polypropylene and a sheath of polyethylene and a third filament having a fineness of 1.5 to 6 denier is needle-punched. And heat-treated without smoothing the web raised state on both sides to produce a cloth-shaped plate-like body having a weight of 200 to 800 g / m 2 and a thickness of 2 to 8 mm,
2. The high-concentration sewage treatment apparatus according to claim 1, wherein the cloth-shaped plate-like body cut into a 3 to 5 mm square is loaded as a filter medium.
【請求項3】 上記硝化槽2に装入したろ材3のろ材層
高と水層高との比率を65:35〜50:50となるよ
うに、上記布形化板状体ろ材を装入したことを特徴とす
る、請求項1および請求項2記載の高濃度汚水の処理装
置。
3. The cloth-shaped plate-shaped filter medium is charged so that the ratio of the filter medium layer height to the water layer height of the filter medium 3 charged in the nitrification tank 2 is 65:35 to 50:50. The high-concentration sewage treatment apparatus according to claim 1 or 2, characterized in that:
【請求項4】 上記硝化槽2の処理水部と脱窒槽1の処
理水流入部とを循環ポンプ9aを介して接続し、処理水
の一部を線速度5〜20m/hで循環するようにしたこ
とを特徴とする請求項1から請求項3記載の高濃度汚水
の処理装置。
4. A treatment water section of the nitrification tank 2 and a treatment water inflow section of the denitrification tank 1 are connected via a circulation pump 9a so that a part of the treatment water is circulated at a linear velocity of 5 to 20 m / h. The high-concentration sewage treatment apparatus according to claim 1, wherein:
JP10197892A 1998-07-14 1998-07-14 Treating device of high concentration sewage Pending JP2000024679A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10197892A JP2000024679A (en) 1998-07-14 1998-07-14 Treating device of high concentration sewage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10197892A JP2000024679A (en) 1998-07-14 1998-07-14 Treating device of high concentration sewage

Publications (1)

Publication Number Publication Date
JP2000024679A true JP2000024679A (en) 2000-01-25

Family

ID=16382036

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10197892A Pending JP2000024679A (en) 1998-07-14 1998-07-14 Treating device of high concentration sewage

Country Status (1)

Country Link
JP (1) JP2000024679A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004141719A (en) * 2002-10-22 2004-05-20 Ebara Corp Treatment method of organic wastewater and equipment therefor

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004141719A (en) * 2002-10-22 2004-05-20 Ebara Corp Treatment method of organic wastewater and equipment therefor

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